• Journal of Chest Surgery
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• 제38권7호
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• pp.496-500
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• 2005

심장판막질환의 외과적 교정에 사용되는 수종의 기계판막들은 각기의 장점들을 주장하고 있으나, 중장기의 임상적 결과에는 유의한 차이를 보이지 않는다. 기계적 기능의 차이를 단순 비교하기는 어려우나 수술 후에 시행한 초음파심음향도로 측정한 판막간 압력차와 유효개구면적을 비교하여 다양한 기계판막들간의 기능을 비교하고자 한다. 대상 뜻 방법: 1995년부터 2003년 사이에 아주대학교병원 흥부외과에서 기계판막으로 치환술을 받았던 345명의 환자들에 사용되었던 396개의 기계판막을 대상으로 후향적 분석을 하였다. 사용되었던 판막으로는 Sorin Bicarbon, SJM, ATS, On-X, 그리고 Edward MRA로 5종류였다. 판막의 위치는 승모판막이 232개, 대동맥판막이 162, 그리고 삼첨판막이 2개였으며, 이중 다중판막치환술이 51예에서 있었다. 수술 후 14일이 지난 후에 시행한 초음파심음향도에서 유효개구면적, 수축기 평균압력차, 그리고 이완기 평균압력차를 지표로 통계학적인 비교분석을 하였다. 결과: 345명의 대상환자중 남자가 178명, 여자가 167이었고, 평균연령은 남자/여자가 $50.6\pm13.9/52.6\pm14.6$세였다. 승모판막의 경우 27mm에서는 MDPG/EOA가 Sorin; $4.2\pm1.5 mmHg/3.0\pm0.9cm^2,\;SJM;\;2.3\pm1.2/3.5\pm0.6$였으며, 31m에서는 Sorin, SJM, ATS, Mmh가 $3.9\pm1.9/2.9\pm0.6,\;3.5\pm1.2/3.0\pm0.6,\;3.4\pm0.8/2.8\p,0.2,\;3.7\pm1.5/2.7\pm0.7$ 였으며, 31mmdptjsms Sorin, SJM, ATS, MIRA가 $3.9\pm1.9/2.9\pm0.6,\;3.5\pm1.2/3.0\pm0.6,\;3.4\pm0.8/2.8\pm0.2,\;3.7\pm1.5/2.7\pm0.7$였으며, 33 m에서는 Sorin, SJM, MIRA가 $4.4\pm0.9/2.5\pm0.4,\;3.4\pm1.5/3.3\pm0.5,\;4.7\pm2.4\3.0\pm0.3$이었다. 대동맥판막의 경우 19mm에서 MSPG/EOA가 Sorin, SJM, ATS, On-X, MIRA가 $18.0 mmHg/1.2cm^2,\;25.6\pm8.7/1.1\pm0.3,\;25.9\pm12.6/1.2\pm0.3,\;23.0/1.3,\;27.9\pm7.1/1.2\pm0.1$였으며, 21mm에서는 SJM, ATS, On-X, MIRA가 $18.3\pm6.7/1.5\pm0.5,\;13.7\pm2.1/1.7\pm0.3,\;17.0/1.4,\;17.1\pm5.5/1.8\pm0.5$였으며, 23 m에서는 Sorin, SJM, ATS On-X, MIRA가 $14.0\pm4.6/1.7\pm0.6,\;12.8\pm3.2/2.0\pm0.2,\;16.8\pm12.2/2.1\pm0.9,\;14.0/1.5,\;15.0\pm5.5/1,8\pm0.5$이었다 25mm에서는 SJM과 MIRA가 $14.0\pm5.1/1.8\pm1.0,\;11.0/2.3$이었다. 통계학적인 분석을 한 결과 같은 위치에 같은 크기의 판막들간에는 통계적으로 유의한 차이가 없었다. 판막재치환을 한 경우는 용혈로 인한 재치환이 ATS에서 1예, 판엽고정에 의한 재치환이 SJM에서 1예 있었다. 결론: 최근 국내에서 흔히 사용되고 있는 5종의 기계판막을 수술 후에 초음파심음향도로 추적조사한 결과 동일한 판막크기에서 각 판막간의 기능적 차이는 없는 것으로 조사되었다.

• 한국환경과학회지
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• 제27권10호
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• pp.925-931
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• 2018

The characteristics of $PM_{10}$, $PM_{2.5}$ and Ratio($PM_{2.5}/PM_{10}$) of 11 urban air monitoring stations in Gyeongnam were analyzed for the last 3 years('15~'17). The average of the all stations was $PM_{10}\;45{\mu}g/m^3$, $PM_{2.5}\;24{\mu}g/m^3$ and Ratio 0.54, and annual reduction rates were $PM_{10}-2.9%$, $PM_{2.5}-2.7%$ and Ratio -1.2%, respectively. The seasonal characteristics of $PM_{10}$ were spring $54{\mu}g/m^3$ > winter $48{\mu}g/m^3$ > summer/autumn $40{\mu}g/m^3$, $PM_{2.5}$ were spring/winter $26{\mu}g/m^3$ > summer 23 > autumn $22{\mu}g/m^3$ and Ratio were summer 0.56 > winter 0.55 > autumn 0.54 > spring 0.51, respectively. The hourly characteristics of $PM_{10}$ were $11{\mu}g/m^3$ higher than 09:00~12:00 at 03:00~06:00, $PM_{2.5}$ were $6{\mu}g/m^3$ higher than 09:00~12:00 at 17:00~18:00 and Ratio were 0.07 higher than 04:00~06:00 at 19:00. By site, the highest concentration of $PM_{10}$ was YJ site $53{\mu}g/m^3$ and $PM_{2.5}$ was HW site $28{\mu}g/m^3$. And Ratio at HD site showed the largest reduction from '15 0.62 to '17 0.52.

• 한국환경과학회지
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• 제17권6호
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• pp.633-645
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• 2008

In order to investigate the variations and corelation among $PM_{10},\;PM_{2.5}\;and\;PM_1$ concentrations, the hourly concentrations of each particle sizes of 300nm to $20{\mu}m$ at a city, Gangneung in the eastern mountainous coast of Korean peninsula have been measured by GRIMM aerosol sampler-1107 from March 7 to 17, 2004. Before the influence of the Yellow Dust event from China toward the city, $PM_{10},\;PM_{2.5}\;and\;PM_1$, concentrations near the ground of the city were very low less than $35.97{\mu}g/m^3,\;22.33{\mu}g/m^3\;and\;16.77{\mu}g/m^3$, with little variations. Under the partial influence of the dust transport from the China on March 9, they increased to $87.08{\mu}g/m^3,\;56.55{\mu}g/m^3\;and\;51.62{\mu}g/m^3$. $PM_{10}$ concentration was 1.5 times higher than $PM_{2.5}$ and 1.85 times higher than $PM_1$. Ratio of $(PM_{10}-PM_{2.5})/PM_{2.5}$ had a maximum value of 1.49 with an averaged 0.5 and one of $(PM_{2.5}-PM_1)/PM_1$ had a maximum value of 0.4 with an averaged 0.25. $PM_{10}\;and\;PM_{2.5}$ concentrations were largely influenced by particles smaller than $2.5{\mu}m\;and\;1{\mu}m$ particle sizes, respectively. During the dust event from the afternoon of March 10 until 1200 LST, March 14, $PM_{10},\;PM_{2.5}\;and\;PM_1$ concentrations reached $343.53{\mu}g/m^3,\;105{\mu}g/m^3\;and\;60{\mu}g/m^3$, indicating the $PM_{10}$ concentration being 3.3 times higher than $PM_{2.5}$ and 5.97 times higher than $PM_1$. Ratio of $(PM_{10}-PM_{2.5})/PM_{2.5}$ had a maximum value of 7.82 with an averaged 3.5 and one of $(PM_{2.5}-PM_1)/PM_1$, had a maximum value of 2.8 with an averaged 1.5, showing $PM_{10}\;and\;PM_{2.5}$ concentrations largely influenced by particles greater than $2.5{\mu}m\;and\;1{\mu}m$ particle sizes, respectively. After the dust event, the most of PM concentrations became below $100{\mu}g/m^3$, except of 0900LST, March 15, showing the gradual decrease of their concentrations. Ratio of $(PM_{10}-PM_{2.5})/PM_{2.5}$ had a maximum value of 3.75 with an averaged 1.6 and one of $(PM_{2.5}-PM_1)/PM_1$ had a maximum value of 1.5 with an averaged 0.8, showing the $PM_{10}$ concentration largely influenced by corse particles than $2.5{\mu}m$ and the $PM_{2.5}$ by fine particles smaller than $1{\mu}m$, respectively. Before the dust event, correlation coefficients between $PM_{10},\;PM_{2.5}\;and\;PM_1$, were 0.89, 0.99 and 0.82, respectively, and during the dust event, the coefficients were 0.71, 0.94 and 0.44. After the dust event, the coefficients were 0.90, 0.99 and 0.85. For whole period, the coefficients were 0.54, 0.95 and 0.28, respectively.

• 한국환경과학회지
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• 제23권5호
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• pp.819-827
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• 2014

This study analyzes the chemical composition of metallic elements and water-soluble ions in $PM_{10}$ and $PM_{2.5}$. $PM_{10}$ and $PM_{2.5}$ concentrations in Busan during 2010-2012 were $97.2{\pm}67.5$ and $67.5{\pm}32.8{\mu}g/m^3$, respectively, and the mean $PM_{2.5}/PM_{10}$ concentration ratio was 0.73. The contribution rate of water-soluble ions to $PM_{10}$ ranged from 29.0% to 58.6%(a mean of 38.6%) and that to $PM_{2.5}$ ranged from 33.9% to 58.4%(a mean of 43.1%). The contribution rate of sea salt to $PM_{10}$ was 13.9% for 2011 and 9.7% for 2012, while that to $PM_{2.5}$ was 17.4% for 2011 and 10.1% for 2012. $PM_{10}$ concentration during Asian dust events was $334.3{\mu}g/m^3$ and $113.3{\mu}g/m^3$ during non-Asian dust events, and the $PM_{10}$ concentration ratio of Asian Dust/Non Asian dust was 2.95. On the other hand, the $PM_{2.5}$ concentration in Asian dust was $157.4{\mu}g/m^3$ and $83.2{\mu}g/m^3$ in Non Asian dust, and the $PM_{2.5}$ concentration ratio of Asian Dust/Non Asian dust was 1.89, which was lower than that of $PM_{10}$.

• 한국산학기술학회논문지
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• 제12권11호
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• pp.4940-4950
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• 2011

고지혈증 치료제인 cis-(3R,5R)-atorvastatin Ca (1)은 4개의 입체이성질체가 있으며, 각각의 이성질체들을 선택적으로 제조한다는 것은 매우 어려운 일이다. 본 연구에서는 입체이성질체 중의 하나인 trans-(3R,5S)-atorvastatin Ca (7)을 초산에서 3,5-diketo atorvastatin ester (3)를 $Me_4NHB(OAc)_3$을 사용하여 환원시켜 cis-(3R,5R) (4)과 trans-(3R,5S)-atorvastatin ester (5)를 각각 1.5%와 98.5%의 비율로 입체선택적으로 제조할 수 있었다. 또한, 고지혈증 치료제인 cis-(3R,5R)-atorvastatin Ca (1)과 그의 입체이성질체인 trans-(3R,5S)-atorvastatin Ca (7)을 쥐에서 고지방식이에 의해 유발된 고지혈증의 치료효과에 대하여 알아보았고, 이러한 연구의 수행을 위해 2010년 1월에 실험을 실시하였다. 그 결과, 화합물 1과 7의 total cholesterol (TC), high-density lipoprotein-cholesterol (HDL-c), low-density lipoprotein-cholesterol (LDL-c)과 triglyceride (TG)는 각각 $93.0{\pm}0.5$, $43.5{\pm}0.8$, $40.4{\pm}1.4$, $45.6{\pm}0.9\;mg/d{\ell}$와 $110.0{\pm}0.7$, $33.3{\pm}0.6$, $65.8{\pm}1.9$, $54.8{\pm}1.2\;mg/d{\ell}$를 atherogenic index (AI)와 cardiac risk factor (CRF)는 $1.14{\pm}0.05$ $2.14{\pm}0.05$와 $2.31{\pm}0.06$, $3.31{\pm}0.06$을 나타냈으며 aspartate aminotransferase (AST)와 alanine aminotransferase (ALT)는 $51.9{\pm}4.6$, $16.0{\pm}2.1\;IU/{\ell}$와 $75.8{\pm}4.4$, $35.1{\pm}9.7\;IU/{\ell}$로 두 화합물 모두 고지혈증에 대한 치료효과를 나타내었으나, 화합물 1이 우수한 치료효과가 있는 반면 화합물 7은 치료효과가 낮은 것을 확인하였다. 이러한 결과들로 입체선택적 이성질체의 합성에 대한 새로운 방법을 제시하고, 향후 시판되고 있는 의약품들의 입체이성질체에 대한 임상적 활용이 가능할 것으로 사료된다.

• 생명과학회지
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• 제18권12호
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• pp.1728-1732
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• 2008

우리나라에서 서식하는 애반딧불이의 생육 특성을 조사한 결과, $23^{\circ}C$, R.H. 80%에서 사육에서 성충 수명은 암컷이 $17.5{\pm}0.7$일, 수컷이 $20.6{\pm}1.0$일으로 수컷이 다소 높았으나, 사육밀도별 유의차는 없었다. 성충 출현 후 최초 산란일은 1쌍 $2.8{\pm}1.5$일, 2쌍 $2.5{\pm}1.5$일, 3쌍 $1.7{\pm}0.7$일, 4쌍 $1.3{\pm}0.5$일로 사육 밀도가 증가함에 따라 산란전기가 짧아졌다. 산란수는 평균 $248.9{\pm}80.7$개를 산란하며, 사육밀도와는 유의성이 없었다. 일별 산란은 산란 시작 1일째가 20.8%, 2일째 17.3%, 3일째 14.3%, 4일째 12.7%, 5일째 7.0%의 순으로 산란 시작 1일째가 가장 높고 시간이 경과함에 따라 점차 낮아졌다. 난기간은 $21.8{\pm}0.7$일이고, 부화율은 $95.5{\pm}4.8%$이었다. 유충 령기 구분은 탈피각과 유충반문으로 조사한 바 9령으로 확인되었고 1령 $1.0{\pm}0.1$일, 2령 $3.3{\pm}0.2$일, 3령 $10.2{\pm}1.0$일, 4령 $6.8{\pm}0.5$일, 5령 $6.9{\pm}2.0$일, 6령 $15.4{\pm}4.1$일, 7령 $18.3{\pm}5.9$일, 8령 $25.8{\pm}8.7$일, 9령 $31.2{\pm}13.2$일이었다. 성숙한 9령 유충은 $2.8{\pm}0.8$일 동안 용실을 만들고, 전용기간과 용기간은 $4.6{\pm}0.9$일과 $5.6{\pm}0.7$일이었으며, 성충이 된 후 약 $3.8{\pm}0.4$일 동안 뒷날개를 굳힌 후 용실을 뚫고 탈출하였다

• 한국환경과학회지
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• 제26권9호
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• pp.1045-1055
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• 2017

Characterization of spatio-temporal variations in $PM_{2.5}$ in Gyeongnam (GN) province during 2015-2016 was investigated to assess the air quality in this area in terms of fine particles. Yearly mean concentrations of $PM_{2.5}$ ranged from 19.1 to $29.5{\mu}gm^{-3}$. High concentrations of $PM_{2.5}$ were observed in spring ($21.2-30.3{\mu}gm^{-3}$) and winter ($20.2-30.3{\mu}gm^{-3}$). Low concentrations of $PM_{2.5}$ were generally observed in fall ($16.2-23.2{\mu}gm^{-3}$). $PM_{2.5}$ concentration was highest in the morning (10 AM). The fractions of $PM_{2.5}$ in $PM_{10}$ were 0.51-0.62 and two were significantly correlated (r=0.779-0.830), suggesting common sources (fossil fuel combustion, mobile sources, etc). CO was significantly correlated with $PM_{2.5}$ in highly urbanized areas such as the city of Changwon (CW, r=0.711), compared to other air pollutants ($SO_2$, $NO_2$, and $O_3$), suggesting dominance of industrial combustion sources.

• 환경영향평가
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• 제16권5호
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• pp.327-340
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• 2007

The $PM_{10}$ and $PM_{2.5}$ aerosols were collected at Busan from March to May, 2005, and the concentrations of some metallic elements were analysed to study their characteristics. The mean concentration of $PM_{10}$ was $66.5{\pm}23.0{\mu}g/m^3$ with a range of 22.2 to $118.1{\mu}g/m^3$. The mean concentration of $PM_{2.5}$ was $46.1{\pm}17.2{\mu}g/m^3$ with a range of 9.7 to $83.3{\mu}g/m^3$. The ratio of $PM_{2.5}/PM_{10}$ was 0.69 at Busan. The distribution of metallic elements for $PM_{10}$ and $PM_{2.5}$ were Cd${\ldots}$ ${\ldots}$ $PM_{10}$ were $94.9{\mu}g/m^3$ and $63.7{\mu}g/m^3$, respectively. And The mean mass concentrations of Asian dust and non Asian dust in $PM_{2.5}$ were $56.9{\mu}g/m^3$ and $45.1{\mu}g/m^3$, respectively. The mean values of crustal enrichment factors for five elements (Cd, Cu, Pb, V and Zn) were all higher than 10, possibly suggesting the influence of anthropogenic sources. The soil contribution ratios for $PM_{10}$ and $PM_{2.5}$ were 20.5% and 19.4, respectively.

• 한국환경과학회지
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• 제24권5호
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• pp.679-687
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• 2015

Atmospheric aerosol particles were investigated at GNTECH university in Jinju city. Samples were collected using the Nanosampler period from January to December 2014. The Nanosampler is a 6 stage cascade impactor(1 stage : > $10{\mu}m$, 2 stage : $2.5{\sim}10{\mu}m$, 3 stage : $1.0{\sim}2.5{\mu}m$, 4 stage : $0.5{\sim}10{\mu}m$, 5 stage : $0.1{\sim}0.5{\mu}m$, back-up : < $0.1{\mu}m$) with the stages having 50% cut-off ranging from 0.1 to $10{\mu}m$ in aerodynamic diameter. The mass size distribution of Atmospheric aerosol particles was unimodal with peak at $1.0{\sim}2.5{\mu}m$ or $0.5{\sim}1.0{\mu}m$. The annual average concentrations of TSP, $PM_{10}$, $PM_{2.5}$, $PM_1$, $PM_{0.5}$ and $PM_{0.1}$ were $44.0{\mu}g/m^3$, $40.3{\mu}g/m^3$, $31.4{\mu}g/m^3$, $18.0{\mu}g/m^3$, $8.0{\mu}g/m^3$, $3.0{\mu}g/m^3$, respectively. On average $PM_{10}$, $PM_{2.5}$, $PM_1$, $PM_{0.5}$ and $PM_{0.1}$ make up 0.91, 0.70, 0.41, 0.19 and 0.07 of TSP, respectively. The annual average of $PM_{2.5}/PM_{10}$ ratio was 0.77.

• 대한원격탐사학회지
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• 제37권6_2호
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• pp.1793-1801
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• 2021

2015년 1월부터 2020년 6월까지 라이다를 이용하여 측정된 532와 1064 nm의 후방산란계수와 532 nm의 편광소멸도를 이용하여 532 nm의 후방산란계수를 PM₁₀, PM_2.5-10, PM_2.5에 해당하는 세 유형으로 구분하고 지상에서 측정된 질량 농도를 이용하여 각각의 질량소산효율을 산출하였다. 산출된 질량소산효율의 전체 평균값은 PM₁₀, PM_2.5-10, PM_2.5에서 각각 5.1±2.5, 1.7±3.7, 9.3±6.3 m²/g으로 PM_2.5가 가장 높은 값을 보였다. PM₁₀과 PM_2.5의 질량 농도가 낮을 때 평균 이상의 높은 질량소산효율이 산출되었으며 질량 농도가 높아질수록 질량소산효율이 감소되는 경향을 확인하였다. 황사의 혼합 정도에 따른 유형별로 질량소산효율을 산출하였을 때, PM_2.5-10는 황사의 영향으로 오염입자(pollution aerosol, PA)가 2.1±2.8 m²/g으로 오염입자가 주요한 혼합입자(pollution-dominated mixture, PDM), 황사가 주요한 혼합입자 (dust-dominated mixture, DDM), 순수황사 (pure dust, PD)의 1.1±1.8, 1.4±3.3, 1.1±1.5 m²/g보다 두 배 정도 높은 값을 보였다. 하지만, PM_2.5는 9.4±6.5, 9.0±5.8, 10.3±7.5, 9.1±9.0 m²/g으로 유형 구분 없이 비슷한 값을 보였다. PM₁₀의 질량소산효율은 PA, PDM, DDM, PD 에서 각각 5.6±2.9, 4.4±2.0, 3.6±2.9, 2.8±2.4 m²/g으로 황사의 비율이 감소할수록 증가하는 경향을 보였다. 동일한 질량 농도 또는 황사 혼합에 따른 동일한 유형을 보이더라도 PM_2.5/PM₁₀ 값이 낮아질수록 PM_2.5-10의 질량소산효율은 감소하고, PM_2.5의 질량소산효율은 증가하는 경향을 보였다.